Circulating fluidized bed reactor with selective catalytic reduction

ABSTRACT

A CFB reactor or combustor having a selective catalytic reduction (SCR) system ( 150 ) employed downstream of the CFB reactor or combustor furnace ( 10 ) together with a dry scrubber system ( 220 ) to achieve enhanced NO x  reduction.

This application is a 371 of PCT/US01/03786 filed Feb. 6, 2001, which is a continuation-in-part of application Ser. No. 09/503,218, filed Feb. 13, 2000, now U.S. Pat. No. 6,395,237.

FIELD OF THE INVENTION

The present invention relates, in general, to circulating fluidized bed (CFB) reactors or combustors and, more particularly, to a CFB reactor or combustor having a selective catalytic reduction (SCR) system employed downstream of the CFB reactor or combustor furnace to achieve enhanced NO_(x) reduction capability.

BACKGROUND OF THE INVENTION

Environmental protection and the control of solid, liquid and gaseous effluents or emissions are key elements in the design of steam generating systems which utilize the heat generated by the combustion of fossil fuels to generate steam. At present, the most significant of these emissions are sulfur dioxide (SO₂), oxides of nitrogen (NO_(x)), and airborne particulate.

NO_(x) refers to the cumulative emissions of nitric oxide (NO), nitrogen dioxide (NO₂) and trace quantities of other species generated during combustion. Once the fuel is chosen, NO_(x) emissions are minimized using low NO_(x) combustion technology and postcombustion techniques. If combustion modifications alone are insufficient, postcombustion techniques such as selective noncatalytic reduction (SNCR) or selective catalytic reduction (SCR) systems may be employed. In SNCR or SCR systems, NO_(x) is reduced to nitrogen (N₂) and water (H₂O) through a series of reactions with a chemical reagent injected into the flue gas. Ammonia and urea are the most commonly used chemical reagents with SNCR systems, while ammonia is most commonly used for SCR systems.

Fluidized bed combustion has distinct advantages for burning solid fuels and recovering energy to produce steam; indeed, the primary driving force for the development of fluidized bed combustors in the United States is reduced S₂ and NO_(x) emissions. Typically, this technology can be used to burn high sulfur coals and achieve low SO₂ emission levels without the need for additional back-end sulfur removal equipment. Fluidized bed boilers are designed so that the bed operating temperature is between 1500 and 1600° F., resulting in lower NO_(x) emissions. These lower operating temperatures also permit combustion of lower grade fuels (which generally have high slagging and fouling characteristics) without experiencing many of the operational difficulties which normally occur when such fuels are burned.

In CFB reactors or combustors, reacting and non-reacting solids are entrained within a reactor enclosure by an upward gas flow which carries the solids to an exit at an upper portion of the reactor enclosure. There, the solids are typically collected by a primary particle separator, of impact type or cyclone type and returned to a bottom portion of the reactor enclosure either directly or through one or more conduits. The impact type primary particle separator at the reactor enclosure exit typically collects from 90% to 97% of the circulating solids. If required by the process, an additional solids collector may be installed downstream of the impact type primary particle separator to collect additional solids for eventual return to the reactor enclosure.

CFB reactors or combustors are known (see, for example, U.S. Pat. No. 5,343,830 to Alexander et al.) wherein the two or more rows of impingement members located within the furnace or reactor enclosure are followed by a second array of staggered impingement members which further separate particles from the gas stream, and return them via cavity means and particle return means without external and internal recycle conduits.

Both SCR and SNCR systems have been applied to reduce NO_(x) emissions from pulverized coal fired steam generating systems. SNCR systems have also been applied to fluidized bed steam generators, and it has been proposed to combine a CFB steam generator for petroleum coke firing with an SCR system.

SUMMARY OF THE INVENTION

The present invention relates generally to the field of circulating fluidized bed (CFB) reactors or combustors and provides a system to achieve low NO_(x) emissions at lowest operating cost. Fluidized bed combustion technologies provide combustion temperatures that are much lower (1550-1600° F.) at the point of fuel admission than in pulverized coal combustion systems, where the combustion temperatures may be 2500-3000° F. This difference in combustion temperature contributes to a large difference in uncontrolled NO_(x) emissions from the fluidized beds Uncontrolled NO_(x) emissions from pulverized coal technologies typically ranges from 0.3 to 0.7 lbs/10⁶ Btu, but NO_(x) emissions from fluidized bed technologies is several times less, typically 0.12-0.2 lbs/10⁶ Btu. However, even more stringent emissions regulations are being encountered, typically on the order of 0.10 lbs/10⁶ Btu. This degree of NO_(x) reduction has been accomplished on fluid bed technologies with SNCR systems (spraying ammonia at locations where the gas temperatures are in the range of 1450-1650° F.), and on pulverized coal technologies with SCR systems (spraying ammonia at locations where the gas temperatures are in the range of 750° F). However, experience with SCR technology has shown that less ammonia is needed for a given reduction in NO_(x) and the unreacted ammonia leaving the system is less than with SNCR technology (usually, 5 ppm with SCR as compared with 25 ppm with SNCR). Since the initial NO_(x) in fluidized bed systems is lower, the NO_(x) after the SCR system can be much lower with only a minimal use of catalyst and ammonia

Accordingly, one aspect of the present invention is drawn to a combination of a CFB reactor or combustor and an SCR system. The combination comprises a CFB reactor enclosure for conveying a flow of flue gas/solids therethrough, primary particle separator means for separating solids particles from the flow of flue gas/solids, and means for returning the solids particles collected by the primary particle separator means to the reactor enclosure. At least one of superheater and reheater heat transfer surface is located downstream of the primary particle separator means with respect to the flow of flue gas/solids. Multiclone dust collector means, located downstream of the at least one of superheater and reheater heat transfer surface, are provided for further separating solids particles from the flow of flue gas/solids, together with means for returning the solids particles collected by the multiclone dust collector means to the reactor enclosure. An SCR system is located downstream of the multiclone dust collector means for removing NO_(x) from the flow of flue gas/solids, and dry scrubber means is located downstream of the SCR system. Finally, means are provided for injecting ammonia into the flow of flue gas/solids upstream of the SCR system to cause the chemical reactions which reduce the NO_(x) emissions.

The various features of novelty which characterize the invention are pointed out with particularity in the claims annexed to and forming a part of this disclosure. For a better understanding of the invention, its operating advantages and specific benefits attained by its uses, reference is made to the accompanying drawings and descriptive matter in which a preferred embodiment of the invention is illustrated.

BRIEF DESCRIPTION OF THE DRAWINGS

In the drawings:

FIG. 1 is a schematic representation of the combination of a circulating fluidized bed (CFB) reactor or combustor and SCR system according to a first embodiment of the invention;

FIG. 2 is a schematic representation of the combination of a circulating fluidized bed (CFB) reactor or combustor and SCR system according to a second embodiment of the invention; and

FIG. 3 is a schematic representation of the combination of a circulating fluidized bed (CFB) reactor or combustor and SCR system according to a third embodiment of the invention.

FIG. 4 is a schematic representation of the combination of a circulating fluidized bed (CFB) reactor or combuster and SCR system according to an embodiement of the invention;

FIG. 5 is a schematic representation of the combination of a circulating fluidized bed (CEB) reactor or combustor and SCR system according to another embodiment of the invention; and

FIG. 6 is a schematic representation of the combination of a circulating fluidized bed (CFB) reactor or combustor and SCR system according to yet another embodiment of the invention.

DESCRIPTION OF THE PREFERRED EMBODIMENTS

As used herein, the term CFB combustor refers to a type of CFB reactor where a combustion process takes place. While the present invention is directed particularly to boilers or steam generators which employ CFB combustors as the means by which the heat is produced, it is understood that the present invention can readily be employed in a different kind of CFB reactor. For example, the invention could be applied in a reactor that is employed for chemical reactions other than a combustion process, or where a gas/solids mixture from a combustion process occurring elsewhere is provided to the reactor for further processing, or where the reactor merely provides an enclosure wherein particles or solids are entrained in a gas that is not necessarily a byproduct of a combustion process.

To the extent necessary to describe the general operation of CFB reactors and combustors, the reader is referred to Chapter 16 of Steam/its generation and use, 40th Edition, Stultz and Kitto, Eds, Copyright© 1992, The Babcock & Wilcox Company, and to U.S. Pat. No. 5,343,830 to Alexander et al., both of which are hereby incorporated by reference as though fully set forth herein. For background information concerning NO_(x) reduction techniques and apparatus in general, and to selective catalytic reduction (SCR) systems in particular, the reader is also referred to the aforementioned Steam text at Chapter 34 thereof, the text of which is also hereby incorporated by reference as though fully set forth herein.

Referring generally to the drawings, wherein like reference numerals represent the same or functionally similar elements throughout the several drawings, and to FIGS. 1-3 in particular, there is shown a circulating fluidized bed (CFB) reactor or combustor, generally designated 10, comprising a reactor enclosure 20 having an upper portion 30. The reactor enclosure 20 is typically rectangular in cross-section and is defined by fluid cooled enclosure walls typically comprised of water and/or steam conveying tubes separated from one another by a steel membrane to achieve a gas-tight reactor enclosure 20.

Fuel 40 such as coal, sorbent 50 such as limestone, and combustion air 60 are provided into the reactor enclosure 20 using means well known to those skilled in the art The combustion process occurring within a lower portion of the reactor enclosure 20 thus produces a flow of flue gas/solids 70 which is conveyed upwardly out of the reactor enclosure 20, passing across several solids particle and heat removal stages, as will be herein described, before being conveyed to the atmosphere.

Located in the upper portion 30 of the reactor enclosure 20, in the direction of the flue gas/solids flow, 70, primary particle separator means 80 are provided to collect solids particles from the flow of flue gas/solids 70 so that they may be returned to a lower portion of the reactor enclosure 20. Preferably, the primary particle separator means 80 comprises an array of staggered, impact type particle separators (not shown). The staggered, impact type particle separators are non-planar; they may be U-shaped, E-shaped, W-shaped or any other shape which presents a cupped or concave surface configuration to the flow of incoming flue gas/solids 70. Alternatively, the primary particle separator means 80 may comprise a cyclone separator of known construction (not shown); in that case, a downstream multiclone dust collector (described intra) would typically not be provided.

Solids particles 90 removed from the flow of flue gas/solids flow 70 are returned to the reactor enclosure 20, either via L-valves, J-valves or via internal recirculation such as is described in U.S. Pat. No. 5,343,830 to Alexander et al., and thus this return is merely schematically indicated in the FIGS.

The flow of flue gas/solids 70 is then conveyed to and across one or more banks of heat transfer surface comprising superheater (SH) and/or reheater (RH) surface 100, and then (in FIGS. 1 and 2) to a secondary stage of particle separation typically employing a multiclone dust collector (MDC) 110. Solids particles 120 removed by the MDC 110 are returned to the reactor enclosure 20 via line 130, and the flue gas/solids 70 is then conveyed to and across one or more banks of economizer (EC) heat transfer surface 140 before being conveyed to an SCR system 150.

Alternatively, as illustrated in FIG. 3, the placement of the MDC 110 and EC 140 may be reversed, such that the flue gas/solids 70 is conveyed from the SH/RH 100 to the EC 140 and then to the MDC 110. In any of the embodiments illustrated in FIGS. 1-3, and as well known to those skilled in the art, the particular amount of EC 140 employed would depend upon the desired flue gas temperature entering the SCR 150 for proper optimum operation. From there, the flow of flue gas/solids 70 would be conveyed to the SCR 150 as before. Means 160 for injecting ammonia into the flow of flue gas/solids 70 at a location upstream of the SCR 150 are also provided.

As illustrated in FIG. 2, it may be possible to combine the injection of urea or ammonia at a suitable location (with respect to temperature, etc.) in the flue gas/solids flow 70 to achieve further NO_(x) reduction.

Upon leaving the SCR 150, the flue gas/solids 70 is then typically conveyed to and across another bank of EC surface, this time designated 170 for clarity, and then to air heater means 180 irk of known design. Air heater means 180 may be of the regenerative or recuperative type. Next, in the direction of flue gas/solids flow 70, a final particulate collection means 190 is provided, and which may comprise either a baghouse or electrostatic precipitator. Particles 200 collected by the particulate collection means 190 may also be returned to the reactor enclosure 20 via line 210. Downstream of the particulate collection means 190 may also be provided a dry scrubber reactor system, generally designated 220, for sulfur capture from the flue gas/solids 70. For a description of dry scrubber systems and their general principles of operation, the reader is referred to Chapter 35 of Steam/its generation and use, 40th Edition, Stultz and Kitto, Eds, Copyright© 1992, The Babcock & Wilcox Company, the text of which is hereby incorporated by reference as though fully set forth herein Finally, an induced draft fan 250 would receive the flue gas/solids 70 and convey it to a stack 260 in known fashion

The present invention recognizes that CaO, produced in the bed of a CFB reactor or combustor, is potentially detrimental to the catalyst used in an SCR system 150. The range of gas/solids analyses that might be expected downstream of the MDC 110 is as follows:

Gas Analysis, Vol. % Solids Analysis, Wt. % CO₂ 14-15 CaO 4-14 H₂O  7-15 CaSO₄ 8-16 O₂  3-4 C 6-10 SO₂ 0.02-0.04 (200-400 ppm) Ash* balance N₂ balance (*major ash constituents are SiO₂, Al₂O₃, Fe₂O₃)

However, if sulfur reduction is performed using limestone feed, there should be less CaO content in the flue gas/solids as the Ca/S ratio for a given sulfur capture is lower in a CFB. Additionally, using a dry scrubber 220 for sulfur capture, as a sole means or along with sorbent feed into the reactor enclosure 20, may be further beneficial in reducing CaO content in any ash particles entering the SCR system 150, thereby further reducing NO_(x) emissions, since CaO works as a catalyst in generating NO_(x). Further, while the dry scrubber 220 has been illustrated in the Figs. as being located downstream of the particulate collection means 190, it may be desirable to reverse the order of these two elements 190, 220, as shown in FIGS. 4-6, to reduce particulate emissions to the atmosphere, and also to permit at least a portion of any unused sorbent (CaO) which may be contained in the flue gas/solids 70 to be introduced into the dry scrubber 220 and thereby provide an additional source of sorbent for use in the sulfur oxides reduction process taking place in the dry scrubber 220.

While a specific embodiment of the invention has been shown and described in detail to illustrate the application of the principles of the invention, it will be understood that the invention may be embodied otherwise without departing from such principles. For example, the present invention may be applied to new construction involving CFB reactors or combustors, or to the repair, replacement, or modification of existing CFB reactors or combustors. In some embodiments of the invention, certain features of the invention may be used to advantage without a corresponding use of other features. Accordingly, all such changes and embodiments properly fall within the scope and equivalents of the following claims. 

1. In combination, a CFB reactor or combustor arrangement and an SGR system, comprising: a CFB reactor enclosure for conveying a flow of flue gas/solids therethrough, primary particle separator means for separating solids particles from the flow of flue gas/solids, and means for returning the solids particles collected by the primary particle separator means to the reactor enclosure; at least one of superheater and reheater heat transfer surface located downstream of the primary particle separator means with respect to the flow of flue gas/solids; multiclone dust collector means, located downstream of the at least one of superheater and reheater heat transfer surface, for further separating solids particles from the flow of flue gas/solids, and means for returning the solids particles collected by the multiclone dust collector means to the reactor enclosure; an SCR system located downstream of the multiclone dust collector means for removing NO_(x) from the flow of flue gas/solids; dry scrubber means located downstream of the SCR system; a sorbent contained in the flue gas/solids; particle collector means located downstream of the dry scrubber means, wherein at least a portion of the sorbent contained in the flue gas/solids is introduced into the dry scrubber means, and provides a means for sulfur oxides reduction therein; and means for injecting ammonia into the flow of flue gas/solids upstream of the SCR system.
 2. The combination according to claim 1, wherein the primary particle separator means comprises an array of staggered, impact particle separators having one of a U-shaped, E-shaped, and W-shaped configuration in cross-section.
 3. The combination according to claim 1, further comprising economizer heat transfer surface located upstream of the SCR system to achieve a flue gas temperature entering the SCR system.
 4. The combination according to claim 1, further comprising at least one of economizer heat transfer surface and air heater means located downstream of the SCR system.
 5. The combination according to claim 1, further comprising air heater means located downstream of the SCR system, and wherein the particle collector means is located downstream of the air heater means.
 6. The combination according to claim 5, further comprising means for returning solids particles collected from the flow of flue gas/solids by the particle collector means and the dry scrubber means to the reactor enclosure.
 7. The combination according to claim 5, wherein the particle collector means located downstream of the air heater means comprises one of a baghouse and electrostatic precipitator.
 8. The combination according to claim 1, further comprising means for injecting one of ammonia and urea in a temperature range of approximately 1450-1650° F. upstream of the SCR system in the vicinity of the at least one of superheater and reheater heat transfer surface.
 9. The combination according to claim 1, further comprising at least one of superheater, reheater, and boiler heat transfer surface within the reactor enclosure.
 10. The combination according to claim 1, wherein the primary particle separator means comprises a cyclone separator.
 11. In combination, a CFB reactor or combustor arrangement and an SCR system, comprising: a CFB reactor enclosure for conveying a flow of flue gas/solids therethrough, primary particle separator means for separating solids particles from the flow of flue gas/solids, and means for returning the solids particles collected by the primary particle separator means to the reactor enclosure; at least one of superheater and reheater heat transfer surface located downstream of the primary particle separator means with respect to the flow of flue gas/solids; an SCR system located downstream of the CFB reactor enclosure for removing NO_(x) from the flow of flue gas/solids; dry scrubber means located downstream of the SCR system; a sorbent contained in the flue gas/solids; particle collector means located downstream of the dry scrubber means, wherein at least a portion of the sorbent contained in the flue gas/solids introduced into the dry scrubber means, and provides a means for sulfur oxides reduction therein; and means for injecting ammonia into the flow of flue gas/solids upstream of the SCR system. 